菲、芘、1,2,4-三氯苯对土壤高等植物根伸长抑制的生态毒性效应

测定了草甸棕壤条件下,菲、芘、１,２,４—三氮苯对高等植物（小麦、白菜、西红柿）根伸长抑制串以及复合污染毒性效应。结果表明,菲、芘、１,２,４—三氮苯浓度与植物根伸长抑制串呈显著线性或对数相关（ｐ＝０．０５）。３种化学品对植物根伸长抑制的强弱顺序为１,２,４—三氮苯＞菲＞芘。这与３种化学品的水中溶解度大小显著相关。小麦是３种供试植物中对有机污染物最敏感植物。菲、芘、１,２,４—三氮苯复合污染主表现为协同作用。     

重金属对土壤中小麦种子发芽与根伸长抑制的生态毒性

测定了4种土壤（红壤、草甸棕壤、暗棕壤和栗钙土）条件下,Cu,Zn,Pb和Cd单一污染对小麦种子发芽与根伸长抑制主及其复合污染效应（暗棕壤条件下）。结果表明,同一浓度下,重金属对小麦根伸长抑制率均明显大于对种子发芽抑制率,植物根对金属污染的生态毒性比种子发芽敏感,土壤有机质和土壤N含量与Cu,Zn,Pb和Cd污染对小麦根伸长抑制率显著负相关（R^2OR=0.91,R^2K-N=0.92),土壤PH和阳离子交换量与Cu,Zn,Pb和Cd污染对小麦根伸长抑制率的相关性不显著（R^2PH=0.62,R^2CEC=0.60),在单一污染对小麦根伸长为刺激作用浓度（较低浓度）或为抑制作用浓度下（较高浓度）,复合污染均表现为协同作用。^     

植物CytP450和抗氧化酶对土壤低浓度菲、芘胁迫的响应

以小麦(Triticum acstivnm)为供试植物,草甸棕壤为供试土壤,以微粒体细胞色素P450及抗氧化酶SOD、POD和CAT酶活性为指标,进行了土壤中菲、芘单一及复合胁迫响应研究.结果初步表明,菲、芘胁迫引起植物体内解毒代谢和抗氧化防御酶反应.菲、芘单一胁迫浓度为1mg kg-1时对细胞色素P450产生显著诱导;4 mg kg-1时P450酶含量明显被抑制,表明低浓度菲、芘单一胁迫对植物代谢解毒系统产生损伤;而菲、芘复合1mg kg-1时P450酶含量明显被抑制,说明菲、芘复合胁迫对植物的代谢解毒具有协同毒性效应.土壤中菲、芘单一胁迫未引起SOD酶活性的明显改变,复合胁迫下SOD酶活性出现微弱下降;菲、芘单一胁迫对CAT和POD酶活性具有显著抑制作用;复合胁迫对CAT产生抑制作用,而POD酶活性并未对菲、芘复合产生增强毒性响应.研究从代谢解毒和抗氧化防御酶系统两方面,为土壤低浓度PAHs污染诊断提供了实验依据.     

铅与对二氯苯复合污染对小麦和大白菜种子发芽及幼苗期生长的毒性

在草甸棕壤条件下,测定了铅(Pb2 )与对二氯苯(PDB)的单一及复合污染对小麦和大白菜种子发芽率、幼苗生物量(鲜重、干重)、芽伸长抑制率和根伸长抑制率的影响。结果表明,对外源污染物的敏感顺序为根伸长抑制率>芽伸长抑制率>幼苗鲜重>发芽率和幼苗干重。Pb2 与PDB复合污染的条件下,Pb2 的浓度为500 mg.kg-1时,Pb2 与PDB处于协同效应。Pb2 的浓度为2 000 mg.kg-1时,Pb与PDB联合毒性比较复杂。但不论对于小麦还是大白菜,Pb与PDB的联合作用更多的是依靠Pb2 的作用而不是PDB的作用。     

不同工艺阶段味精废水对作物种子发芽和根伸长的毒性效应

为了对味精废水的污染进行全面的评价,针对不同工艺阶段排放的味精废水,采用小麦、白菜和西红柿等作物种子,以污水为环境介质,进行了种子发芽和根伸长的污染暴露实验,并结合污染现场,进行了相应的定量分析.结果表明,在高浓度原味精废母液中, 小麦种子的发芽抑制率和根伸长的抑制率与废水的浓度呈显著正相关.味精废水对3种作物种子的发芽和根伸长的毒性强弱顺序为：西红柿＞白菜＞小麦西红柿对味精废水毒性响应最为敏感,可以认为是一种较为理想的生物毒性指示作物.味精生产不同工艺阶段所排放的污水对这3种作物种子的发芽半抑制浓度(IC₅₀)为22.0～32432 mg·L^-1,对根伸长的半抑制浓度(IC₅₀)为17.3～3320 mg·L^-1.     

小麦不同生育时期Cd、Cr、Pb污染监测指标体系

以小麦为供试材料,分别采用发芽试验、溶液培养、土柱栽培等毒理试验方法,研究了小麦萌芽期、幼苗期及成株期受重金属污染毒害的指标体系。结果表明,①小麦根伸长抑制率可作为萌芽期重金属污染评价的一项生物指标;Cd、Cr、Pb对小麦根生长的7d半效应浓度(EC50)值分别为1.39、0.20mmo.lL-1和2.75mmol.L-1,据此得到3种重金属对小麦同一性状的毒性次序为CrCdPb;此外各性状抑制率与胁迫浓度的关系可用双曲线模型y=x/(a+x/100)或指数曲线模型y=a(1-exp(-bx))较好模拟。②Cd、Cr、Pb单一污染胁迫对小麦幼苗性状的毒性次序均以影响叶面积和冠部干重为主,表明叶面积和冠部干重为幼苗期污染监测的敏感指标;重金属对除根干重外所有性状的毒性次序:CrCdPb,该毒性次序是根据引起50%抑制的临界浓度即EC50值确定的;各性状抑制率与胁迫浓度的关系可用直线模型、或双曲线模型、或指数曲线模型较好模拟。③重金属单一污染胁迫造成小麦籽粒产量下降幅度是CdCrPb;二元互作对产量影响的重要性次序为CdCrCdPbCrPb;在Cd、Cr、Pb复合污染胁迫条件下,穗数可以作为成株期重金属污染监测的首选指标。以上指标可为农田小麦重金属污染的监测和综合治理提供一些理论依据。     

植物根对土壤中PAHs的吸收及预测

研究了多种植物根对土壤中多环芳烃(PAHs)的吸收作用,阐述了根系吸收与土壤污染强度、污染物性质、植物组成等的关系,并用实验数据检验了限制分配模型对植物吸收土壤中PAHs的预测性能。供试土壤中菲和芘的起始浓度分别为0~457和0~489mg/kg;45d后,随土壤中菲和芘浓度提高,根中菲和芘含量明显增大,根系富集系数则减小。不同植物根中菲和芘含量和根系富集系数与根的脂肪含量呈显著正相关。由于芘的Kow较大,同种植物根中芘含量、芘的根系富集系数则远大于菲。经45d处理,尽管土壤中菲浓度变化很大(从不足1mg/kg到约45mg/kg),限制分配模型能较好地预测供试植物根中菲的含量,黑麦草和菜心根中菲含量的预测误差低于81%。作为限制分配模型预测植物吸收的关键参数,不同植物根吸收菲的αpt值与根脂肪含量显著正相关。     

植物对水中菲和芘的吸收

以菲和芘为多环芳烃（PAHs）代表物,采用水培体系研究了黑麦草（Lolium multiflorum Lam）对水中PAHs的吸收作用,重点研究了植物吸收菲和芘的时间动态.水中菲和芘起始浓度分别为1.00mg/L和0.12mg/L.0～288h内,黑麦草根和茎叶中菲和芘含量均先快速增加而后降低,积累量不断增大,植物根系和茎叶富集系数则先快速升高而后趋于稳定.茎叶中菲和芘含量、茎叶对菲和芘的富集系数比根低1～3数量级,积累量也明显小于根系.黑麦草根系对水中芘有更强的富集能力,其根系富集系数比菲大85%～179%;而其茎叶对菲的富集作用则略强.菲和芘在植物体内有明显的传导作用.0～288h,传导系数（TF）先显著升高而后趋于恒定;但实验条件下,菲和芘的TF值均很小,分别不高于0.031和0.009,且芘的TF值明显小于菲,表明供试植物对芘的传导能力更弱.     

石油污灌土壤污染物的残留与生态毒理

土壤样品采自沈阳东部石油污水灌渠的上、中、下游。进行了污染物 (Cd、矿物油 )含量分析和生态毒性试验。重金属采用原子吸收分光光度仪测定 ,矿物油采用紫外分光光度计测定。生态毒性试验分别参照国际标准组织 (ISO)和OECD指南 ,进行了植物毒性试验和蚯蚓毒性试验。植物试验以小麦种子发芽根伸长抑制率为试验终点 ,试验周期 5 0h ,蚯蚓毒性试验以蚯蚓死亡率和体重增长抑制率为试验终点 ,试验周期 2 8d。结果表明 ,所有土壤均有矿物油积累 ,含量为 6 6 2 2～ 1391 14mg·kg-1,重金属Cd略高于土壤背景值 ,含量为 0 0 6～ 0 37mg·kg-1。然而 ,土壤对高等植物表现有不同程度的生长刺激效应 ,对蚯蚓有急性致死及慢性亚致死效应。种子发芽根伸长抑制率为 - 2 8 6 1%～ - 5 4 6 5 % ,蚯蚓 2 8d死亡率最大值为 10 %。蚯蚓 14d和 2 8d体重增长抑制率分别为 - 5 13%～ - 2 8 0 5 %和 - 31 78%～ 8 0 8%。研究表明 ,长期石油污水灌溉土壤中矿物油的低积累和较明显的生态毒性。     

中性环境中铝盐絮凝剂对典型作物的生态毒性效应

采用种子发芽和根伸长抑制的陆生生态毒理方法,在中性条件(pH=7.0)下对铝盐絮凝剂(AlCl₃)的生态毒性效应进行了研究.结果表明,AlCl₃溶液在pH=7.0时,与其酸性条件(pH=4.0)相比对萝卜、白菜和小麦等受试作物种子发芽和根伸长均表现出抑制作用,且发芽抑制率和根伸长抑制率与铝浓度均呈极显著相关(P＜0.01).尽管在酸性条件下AlCl₃对白菜和小麦根伸长抑制效应比相同浓度中性条件更为强烈,但对萝卜根伸长的抑制程度在相同铝浓度条件下则是pH=7.0时明显大于pH=4.0时,在低浓度时萝卜发芽抑制率也是中性条件明显高于酸性条件.同时,铝盐在中性条件下对萝卜、白菜的发芽和根伸长产生明显抑制效应的起始浓度低于酸性条件(＜2.0 mg·L^-1).     

用EROD研究苯并芘和六氯苯的联合毒性作用

用7-乙氧基异叻唑酮-脱乙基酶(EROD)检测的方法,研究了苯并芘和六氯苯对日本青鳉肝脏EROD酶的比活力的影响。结果表明,苯并芘和六氯苯对EROD酶的比活力均有激活作用,在实验浓度范围内,EROD酶的比活力与两者浓度之间存在剂量-效应关系。苯并芘和六氯苯表现为一定的协同作用。实验同时发现日本青鳉在六氯苯和苯并芘中暴露后,EROD酶的比活力开始有一个短暂的降低,然后持续升高。对六氯苯和苯并芘暴露的最佳时间进行了探讨。     

Influence of Phenol and Phenanthrene on the Growth of Phalaris arundinacea and Phragmites australis

In constructed wetlands for the treatment of industrial effluents and in contaminated waterlogged soils, wetland plants (helophytes) are exposed to toxic chemicals. Hence, the plants' resistance to contaminants is an important prerequisite for applying phytoremediation to solve these environmental problems. For toxicity tests on the germination and growth of various helophytes (Phalaris arundinaceae and Phragmites australis), phenol, phenanthrene, and a mixture of both were used as examples of chemicals from the petrol- and coal-processing industries. The germination rate, shoot length, root length, and influence on leaves, young shoots, and dry weight were studied. Although an increase in contaminant concentration decreased plant growth (dry weight, shoot length); interestingly, the number of young shoots rose. Low contaminant concentration (about 50 mg/l in case of phenol) stimulated the plant growth. The cress seed germination test was less susceptible compared with plantlet exposure in the case of phenol and phenanthrene. Due to its low bioavailability, solid phenanthrene (without solutizer) did not significantly affect plant growth.     

重金属对土壤中萝卜种子发芽与根伸长抑制的生态毒性

高等植物是生态系统中的基本组成部分。一个平衡、稳定的生态系统生产健康、优良的高等植物。反之 ,一个不稳定或受到外来污染的生态系统 ,对高等植物的生长可带来不利和可见的负面影响。因此 ,利用高等植物的生长状况监测土壤污染程度 ,是从生态学角度衡量土壤健康状况 ,评价土壤质量的重要方法之一[4 ,6] 1) 。土壤生态毒理学评价方法是对化学分析方法的重要补充。目前已建立的高等植物毒理试验有三种方法 ,即 1根伸长试验 ;2种子发芽试验 ;3早期植物幼苗生长试验[3 ,5,6,10 ] 。最初 ,这类试验主要用于纯化学品的毒性检验 ,但随着对土壤…     

多环芳烃降解菌筛选及其降解特性

通过选择性富集培养,从辽河油田稠油污染土壤4号土样中,获得了能以高浓度菲(2000mg·L^-1)为唯一碳源和能源快速生长的优势菌系和优良菌株ZL5．16S rDNA核苷酸序列分析表明,ZL5菌株归类于鞘氨醇单胞菌属,分得的菌系和菌株有较强的降解菲能力,120h混合菌系降解了投加菲的95．28％,菌株降解了69．24％,但它们对芘的降解能力均较低,外加碳源葡萄糖可提高菌系和菌株的菲、芘降解能力,加量多。提高幅度大,但超过一定量。降解速率开始下降,表现出抑制效应。所以,应用时需控制适宜的浓度。     

Degradation of straight-chain aliphatic and high-molecular-weight polycyclic aromatic hydrocarbons by a strain of Mycobacterium austroafricanum

AIMS: Our goal was to characterize a newly isolated strain of Mycobacterium austroafricanum, obtained from manufactured gas plant (MGP) site soil and designated GTI-23, with respect to its ability to degrade polycyclic aromatic hydrocarbons (PAHs). METHODS AND RESULTS: GTI-23 is capable of growth on phenanthrene, fluoranthene, or pyrene as a sole source of carbon and energy; it also extensively mineralizes the latter two in liquid culture and is capable of extensive degradation of fluorene and benzo[a]pyrene, although this does not lead in either of these cases to mineralization. Supplementation of benzo[a]pyrene-containing cultures with phenanthrene had no significant effect on benzo[a]pyrene degradation; however, this process was substantially inhibited by the addition of pyrene. Extensive and rapid mineralization of pyrene by GTI-23 was also observed in pyrene-amended soil. CONCLUSIONS: Strain GTI-23 shows considerable ability to mineralize a range of polycyclic aromatic hydrocarbons, both in liquid and soil environments. In this regard, GTI-23 differs markedly from the type strain of Myco. austroafricanum (ATCC 33464); the latter isolate displayed no (or very limited) mineralization of any tested PAH (phenanthrene, fluoranthene or pyrene). When grown in liquid culture, GTI-23 was also found to be capable of growing on and mineralizing two aliphatic hydrocarbons (dodecane and hexadecane). SIGNIFICANCE AND IMPACT OF THE STUDY: These findings indicate that this isolate of Myco. austroafricanum may be useful for bioremediation of soils contaminated with complex mixtures of aromatic and aliphatic hydrocarbons.     

Removal of surfactant solubilized polycyclic aromatic hydrocarbons by Phanerochaete chrysosporium in a rotating biological contactor reactor

White rot fungi can oxidize surfactant solubilized polycyclic aromatic hydrocarbons (PAH). The objective of this study was to evaluate the performance of immobilized white rot fungus, Phanerochaete chrysosporium, to remove surfactant Tween 80 solubilized PAH i.e. phenanthrene, pyrene and benzo(alpha)pyrene in a rotating biological contactor (RBC) reactor. Results indicated that the immobilized P. chrysosporium in the RBC reactor system in continuous operation could effectively remove the three tested PAH at specific hydraulic loading rates and concentrations tested for each individual PAH. Batch operation of RBC reactor showed that the immobilized P. chrysosporium was stable and effective for the eight successive batch treatments of PAH in solution medium i.e. PAH removal was greater than 90% after 60 h, although only low levels of ligninolytic enzyme activity were detected. The removal of phenanthrene and pyrene in solution medium has been found to be a first order reaction in batch operation. A mass balance calculation indicated that biological oxidation was the main factor for removal of benzo(alpha)pyrene i.e. 95.7% in the RBC reactor. However, for phenanthrene and pyrene, both biological oxidation (i.e. 49 and 56%, respectively) and RBC disc foam adsorption (i.e. 44 and 34%, respectively) made a significant contribution to the removal of PAH.     

Degradation of phenanthrene, fluorene, fluoranthene, and pyrene by a Mycobacterium sp.

Mycobacterium sp. strain BB1 was isolated from a former coal gasification site. It was able to utilize phenanthrene, pyrene, and fluoranthene as sole sources of carbon and energy and to degrade fluorene cometabolically. Exponential growth with solid phenanthrene, pyrene, and fluoranthene was obtained in fermentor cultures. The growth rates were 0.069, 0.056, and 0.040 h-1, respectively. Several metabolites of phenanthrene and fluorene metabolism were identified.